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  • Review on Ecology of Rain Forest

  • Department of Botany, Bioinformatics and Climate Change Impacts Management, School of Sciences, Gujarat University, Navrangpura, Ahmedabad – 380009

Abstract

Rich and varied ecosystems found close to the equator are known as tropical rainforests, or tropical wet evergreen forests. With a complex interplay of biotic, soil, topographic, and climatic elements, these woods are distinguished by their high biodiversity and distinctive ecosystem. High levels of atmospheric moisture, substantial rainfall, and high, comparatively steady temperatures all contribute to the growth and complexity of rainforests. Although the soil in these forests is usually deficient in nutrients, it is quite effective at recycling organic matter. The fauna of rainforests consists of a variety of animal species, such as birds, mammals, reptiles, and amphibians, while the flora consists of a variety of plant species, including epiphytes, palms, and carnivorous plants. All of these species are essential to preserving ecological equilibrium. The study of these forests highlights the significance of comprehending rainforest ecosystems for conservation and management by illuminating the complex interactions between environmental elements and the organisms that call them home.

Keywords

Rainforest, Biodiversity, Ecology

Introduction

The tropical rainforest is the place on Earth where the most different kinds of plants and animals live. It is also known as a tropical wet evergreen forest. This special forest is   found near the equator, where it rains a lot—more than 2,000 mm every year! It only has a few short dry weeks when it doesn’t rain much. Because of all the rain, the plants grow really well, and most of the trees stay green all year long (Mudappa, D., & Raman, T. R. S. (2010). On the forest floor, you can find many plants like herbs, shrubs, ferns, and flowers called orchids. Some plants, known as epiphytes, even grow on the branches of other trees! The bark of trees and the surfaces of leaves are home to tiny plants, fungi, and mosses. All these different plants create a rich environment that supports many animals, from tiny bugs in the soil to big animals like elephants and birds called hornbills. All these living things work together to make the rainforest a special place (Mudappa, D., & Raman, T. R. S. (2010) Tropical rainforests are the most complex ecosystems on Earth. For literally millions of years, rainforests—which many people refer to as jungles—have dominated tropical flora. There may be a diversity of organisms beneath their soaring canopy that is unmatched anywhere else on the planet. (Park, C.C. 1992). High temperatures with little variation throughout the year are found in rainforest regions. Throughout the year, temperatures hover around 20°C to 28°C, with the warmest months in a particular location maybe being a degree or so warmer than the coldest. Because the sun lies primarily above, there are not many fluctuations in the length of daylight throughout the year, which leads to this homogeneity. (Baur, G. N. (1964) Rainforest can be defined as a closed community of essentially, but not exclusively, broadleaved, evergreen, hygrophilous trees, usually with two or more layers of trees and shrubs, and with dependent synusiae of other life-forms, such as climbers and epiphytes.   (Baur, G. N. (1964)

Climate of Rainforest

A variety of meteorological elements that are crucial to the growth of any vegetation make up the climate. At its core, it is a measurement of the atmosphere's capacity to supply the environment with heat, moisture, airflow, and light. (Baur, G. N. (1964) Climate exerts a strong influence over the broad distribution of rainforests within the tropics. It also has a marked effect on regional patterns and structures of rainforest vegetation and habitat. Rainforests occur in hot moist climates. They receive more solar radiation throughout the year than any other vegetation zone on earth, which promotes the rich variety and luxurious character of vegetation. (Baur, G. N. (1964) The typical rainforest climate has two main distinguishing features—relatively constant temperatures, and heavy rainfall. Tropical forests grow under a narrow range of temperatures but a fairly wide range of precipitation. The combination of these two climatic controls secretes the very special environment for rainforest growth Temperatures in rainforest areas are high, and they vary relatively little throughout the year. Temperatures remain fairly constant at between 25°Cand 30°C through the year, the warmest months perhaps a degree or so higher than the coldest months in a given place. This uniformity occurs because the sun is mostly overhead, so variations in the length of daylight throughout the year are limited. (Aiken, S. R., & Leigh, C. H. (1986).

RAINFALL

Rainfall is important ecologically by providing a crude, though nonetheless most convenient, measure of the capacity of the site to supply moisture for the growth of plants. (Baur, G. N. (1964) the rainfall limits for evergreen seasonal rainforest in tropical America are stated to be an annual total of 70 inches, with three months each under 4 but over 2 inches, and to be between 50 and 70 inches, with five months each under 4 inches but over 1 inch. (Richards, p. 317).  In Nigeria, (Keay 0959a) gives an annual rainfall of 48 inches as marking the boundary of the rainforest zone, though this value is modified by humidity. In the tropics, rainforests can be found far beyond these minima along stream banks and in other places where the topography or soil provides favourable moisture conditions. They may not be present in wetter regions where the soil has a limited ability to hold onto moisture. (Baur, G. N. (1964) Thus, the excessively drained limestone soils in parts of the West Indies carry semi -deciduous forest formations though the annual rainfall exceeds 60 inches, and the seasonal drought is not lengthy (Beard, 1946a; Gleason and Cook, 1926) On the other hand, well developed evergreen seasonal rainforest occurs on the deep, well structured, heavy textured soils of the "Planalto" (low plateau) around the C. B.A. station near Santarem, on the Amazon River, though apparently reliable records from C. B.A. stretching over eleven years indicate a mean annual rainfall of only 34 inches, with seven months under 4 inches.

Other Atmospheric Moisture

The site receives atmospheric moisture from a variety of sources, including rainfall, and atmospheric moisture has a variety of ecological effects. While the amount of moisture vapor in the air can have a significant impact on the evapotranspiration rate, tiny amounts of moisture can also be obtained by condensation in the form of dew and mist, as well as from snow and hail falls as one advances farther from the tropics. Snow is by no means unusual in the temperate climate zone where rainforests occur, but it cannot be considered an essential supply of moisture for rainforests, with the possible exception of some of the very high latitude temperate rain forests in South America. (Baur, G. N. (1964). Snowfalls are therefore sporadic above 2,500 feet and nearly yearly above 3,500 to 4,000 feet in northern New South Wales (lat. 28–32° S), where even subtropical rainforests still exist in a few locations. Unusually high snowfalls at these elevations are likely to cause some of the crown damage to rainforest trees.  (Baur, G. N. (1964). Although the incredibly abundant epiphyte flora of Montaine rainforests should be largely attributed to the frequent mists that envelop most tropical mountains, atmospheric water vapor is generally of relatively little importance as a direct source of moisture for plant growth. Similar effects can be seen in the temperate rainforest zones. However, by lowering evapotranspiration rates, especially during times of low rainfall, atmospheric water vapor can have a significant ecological impact. (Baur, G. N. (1964). In rainiest areas, relative humidity is typically high and approaches saturation point most evenings. Nonetheless, throughout the day, particularly during the dry seasons, quite low humidity levels are possible. Therefore, during the dry season, the extremely dry "harmattan" wind that sweeps southward over West Africa from the Sahara can significantly lower the relative humidity in the rainforest belt for a few days at a time and Keay (1959a) considers that the low humidities associated with this phenomenon are as important as rainfall in determining the limits of rainforest occurrence in Nigeria.

Temperature

Given its extensive latitudinal and altitudinal range, rainforests in all of their varieties should be able to withstand a wide range of temperatures. Both latitude and altitude affect the mean yearly temperature. Up to roughly 15 latitudes, the mean temperatures for low altitude stations vary very little. After that, they progressively drop to the area around the geographic tropics, and then they increase steadily as latitude increases. Similar to this, the temperature in mountains drops rather steadily as height rises. The exact rates of temperature decline vary significantly depending on the local land and sea configuration; on average, values seem to be about a 1° F drop in mean temperature for every degree of height gain or for every 250–300-foot increase in elevation.  (Baur, G. N. (1964). Compared to tropical species, temperate species grew at their fastest rates at cooler temperatures. Nonetheless, throughout the temperature range employed, there was a significant overlap in the growth rates of the tropical and temperate rainforest types. Changes in biomass allocation were linked to the maximum growth of the tropical rainforest types, while there were no discernible changes in biomass allocation across the temperature range for the temperate rainforest types. (Baur, G. N. (1964).

Soil

Light is the microclimatic component that most likely exhibits the widest range of circumstances within a rainforest, from the upper canopy to the ground level. Similar to vegetation, soil type is not an independent environmental element in and of itself; rather, it is the outcome of other factors interacting with the parent material of the soil, which is one of the independent factors influencing vegetation. (Baur, G. N. (1964).Plant growth depends on soil in a number of ways. In addition to directly or indirectly supplying the nutrients and moisture that plants need, it offers the physical support and anchorage essential before any tree growth is feasible. (Baur, G. N. (1964). An important "ecological service" is provided by the ecosystem processes that take place in the soil, where 60 to 90% of terrestrial primary production is broken down. Detritivores soil animals are essential to decomposition because they break up litter, crop microbial populations, which increases their metabolism (MacLean, C. D. (1988). Macrofauna can process up to 30% of the annual dead organic matter input to most soils (Dangerfield, 1990) and termites alone have been recorded to consume about 20% of litterfall in Ghanaian forests (Usher, 1975) the paedogenetic mechanisms that result in the landscape's various soil types. Physiography had an impact on pedogenesis, which led to a variety of soil types throughout the terrain. Depending on the location of the Pedon’s on the landscape, distinct soil types were created when comparable parent material was present because of varying exposure to morphogenesis processes such eluviation, illuviation, deposition, cementation of Pedi sediments, and multiple stratification.  (Ande, O. T. (1995).  The bulk of dry land rainforest soils are the result of the combined processes of laterization and podsolization. Both are linked to the quick draining of soil bases, which causes the apparent paradox of incredibly lush flora flourishing on the majority of barren soils, especially in the tropics. (Barnard, R. C. (1956). The roots of the rainforest plants are largely confined to the upper soil layers, but in well drained soils may ramify to a depth of six feet (Beveridge 1957) As previously mentioned, rainforest soils typically, though not always, lack plant nutrients, and it is likely that fertility—more than any other factor—provides the primary production limit for rainforest sites over substantial areas. Although the plants are obviously well suited to using the nutrients that are available as efficiently as possible, it is evident that the species that are found on the most infertile rainforest soils—such as tropical podsol’s and peat swamps—are primarily chosen based on their capacity to withstand low nutrient levels. (Baur, G. N. (1964).

Topography

Topography is the independent environmental component. Climate and soil work together to influence the vegetation, and while topography has a significant local impact.  it has a less significant role overall in determining the composition and structure of rainforests than the other two categories of elements. In actuality, the effects of topography can be roughly divided into two divisions based on how they alter the climatic and edaphic elements, respectively. A few instances should be enough to demonstrate these effects. (Baur, G. N. (1964). topography can significantly change the climate of regions that are geographically close to one another and within the same altitude range at a more local level. This can happen in a number of ways and involves various climatic characteristics. One of the most significant effects of topography on vegetation distribution is wind exposure, which is mostly dictated by topography climatic conditions in the higher topographic positions adjoining these fringing belts of rainforest are suitable for the developing of rainforest, as in the "derived savanna “region of Nigeria (Keay, 1959a) There are additional functions of topography in managing rainforests. The topography has a significant impact on compartment subdivision. A rectangular subdivision can be superimposed almost at will in the even relief of the southern Nigerian rainforests or the Amazonian Planalto, but this is impractical in hilly or mountainous topography, like that found in Malaya, and compartments must be based on local relief features. (Barnard, R. C. (1955) The report on silvicultural systems for rainforest in the Asia-Pacific region (F.A. 0., 1960b) notes that one of the factors favouring mechanized logging is the occurrence of flat topography, while in the mountainous rainforest terrain of Ceylon tractor logging is forbidden

Biotic Factor

Like all forest communities, rainforests are made up of plants, provide shelter to a variety of animals, including humans, and maintain a rich fauna of invertebrate’s microscopic microorganisms in the soil beneath them. Together, these make up the biotic factor, which is partially dependent on the rainforest itself and partially independent of the local flora and fauna. As with the other environmental factors, an understanding of the significance of this factor is necessary before any attempt to manage the rainforest can be made. (Baur, G. N. (1964).

Flora

The most divers forest on earth is the tropical rainforest, which is home to large-buttressed,

Broad leaved trees as well as climbers, epiphytes, and hemi epiphytes. They are rich in flora diversity and feature a multi-layered canopy, which includes upper, intermediate, and dense understory vegetation composition. A vast array of plant species can be found in tropical rainforest. Four different tree layers – emergent, upper canopy, understory, and forest floor make up the vegetation species composition of rainforests. (Baur, G. N. (1964).

Sr no

Common name

Scientific name

Habit

Habitat

1

Kapok Tree

Ceiba pentandra

(L.) Gaertn. [2]

Tall deciduous tree

Tropical rainforests of Central & South America

2

Rubber Tree

Hevea brasiliensis

Müll.Arg.

Tall tree

 

Amazon rainforest; Brazil, Peru

3

golden fig

Ficus aurea

Nutt.

Climbing tree

Southeast Asia, Central America

4

Brazil Nut Tree

Bertholletia excelsa

Humb. & Bonpl.

Emergent tree

Amazon rainforest

5

Banana Plant

Musa acuminata

Colla [2]

Herbaceous plant

Tropical Asia, South America

6

Giant Water Lily

Victoria amazonica

(Poepp.) J.C. Sowerby

Floating aquatic plant

Amazon River basin

 

7

Rafflesia

Rafflesia arnoldii R.Br.[1]

Parasitic flowering plant

Southeast Asian rainforests

8

Balsa Tree

Ochroma pyramidale

(Cav. ex Lam.) Urb.[1

Fast-growing tree

 

Central & South American rainforests

9

Heliconia

Heliconia spp.

Herbaceous perennial

Central & South America, tropics

10

Liana Vines

 

Woody vine

All tropical rainforests

11

Cocoa Tree

Theobroma cacao

L. [1]

Small tree

South American rainforests

12

Orchid

Orchidaceae family

Epiphyte/herbaceous

 

Tropical forests worldwide

13

Fern Tree

 

Cyathea spp.

 

Tree fern

Tropical/subtropical rainforests

 

14

Pitcher Plant

Nepenthes mirabilis

(Lour.) Druce (1869) [a]

Carnivorous climber

Southeast Asia, Borneo, Sumatra

15

Bromeliads

Bromeliaceae family

Epiphyte/herbaceous

Neotropics, especially Central & South America

16

Walking Palm

Socratea exorrhiza

(Mart.) H.Wendl.

Palm tree

Central & South American rainforests

17

Bamboo

Bambusoideae subfamily

Woody grass

Southeast Asia, South America

18

Mahogany

Swietenia macrophylla

King

Hardwood tree

Central & South America

19

Cannonball Tree

Couroupita guianensis

Aubl.[2]

Flowering tree

 

South American rainforests

20

Monkey Brush Vine

Combretum rotundifolium Rich.

Climbing vine

 

Amazon Basin

Fauna

With their ability to pollinate a wide range of plant species, disperse seeds, control pest populations and lessen the damage caused by various pest species, scavenge carcasses, and recycle nutrients back into the soil, faunas play a crucial role in the ecosystem of tropical rainforests and offer a wide range of environmental services. (Baur, G. N. (1964).

 

Common name

Scientific name

Category

Notes

1

Jaguar

Panthera onca

Mammal (Carnivore)

Apex predator; excellent swimmer

2

Harpy Eagle

Harpia harpyja

Bird of prey

One of the world’s strongest eagles

3

Sloth (Brown-throated)

Bradypus variegatus

Mammal (Herbivore)

 

Extremely slow-moving, arboreal

4

Poison Dart Frog

Dendrobates spp.

Amphibian

 

 

Brightly colored; toxic skin

5

Anaconda (Green)

Eunectes murinus

Reptile (Snake)

 

largest snakes on Earth

 

6

Toucan

Ramphastos spp.

Bird (Frugivore)

Known for large, colourful beak

7

Gorilla

Gorilla spp.

Mammal (Herbivore)

Largest living primate

8

Okapi

Okapia johnstoni

Mammal (Herbivore)

 

Forest-dwelling relative of the giraffe

9

Orangutan

Pongo spp.

Mammal (Omnivore)

 

Highly intelligent great ape

10

Aye-Aye

Daubentonia madagascariensis

Mammal

Nocturnal lemur with unique finger for foraging

11

Sun Bear

Helarctos malayanus

Mammal

 

Smallest of all bear species

12

Glass Frog

Centrolenidae family

 

Amphibian

Transparent skin on underside

13

Tiger

Panthera tigris

Mammal

Apex predator

14

Bushmaster Snake

Bushmaster Snake

Reptile (Venomous)

One of the largest pit vipers

15

Goliath Beetle

Goliathus spp.

 

Insect

 

One of the largest insects in the world

16

Macaw (Scarlet)

 

Ara macao

Bird

 

Social, brightly coloured parrot

17

Howler Monkey

 

Alouatta spp

Mammal

Loudest land animal

18

Red-eyed Tree Frog

 

Agalychnis callidryas

Amphibian

Famous for vivid coloration

19

Leafcutter Ant

Atta spp.

Insect

Farmers of fungus; complex societies

20

Amazon River Dolphin

Inia geoffrensis

 

Mammal (Aquatic)

Pink freshwater dolphin

CONCLUSION

A complex and dynamic ecosystem, the tropical rainforest is influenced by biotic interactions, terrain, soil characteristics, and climate. Numerous plant and animal species can flourish in the ideal conditions created by the consistent warmth and wetness. In addition to adding to the rainforest's natural beauty, its abundant biodiversity is essential for controlling the planet's climate, harbouring innumerable species, and supplying ecosystem services like water and carbon sequestration. However, the existence of these ecosystems is threatened by their delicate nature as well as human actions like deforestation and climate change. Implementing sustainable management practices and increasing public understanding of the value of tropical rainforests are crucial to preserving them and the priceless services they offer. To ensure these forests' long-term survival and the preservation of the planet's biodiversity, more research into the complex relationships within them is essential

REFERENCE

  1. Aiken, S. R., & Leigh, C. H. (1986). Land use conflicts and rain forest conservation in Malaysia and Australia: The Endau-Rompin and Gordon-Franklin controversies. Land Use Policy, 3(3), 161-179.
  2. Ande, O. T. (1995). Morphogenetic characterization of upland soils in south western Nigeria (Doctoral dissertation, MSc. Thesis, Unpublished. Obafemi Awolowo University, Ile Ife, Nigeria).
  3. Barnard, R. C. (1955). Silviculture in the tropical rain forest of western Nigeria compared with Malayan methods. Empire Forestry Review, 34(4), 355-368.
  4. Barnard, R. C. (1956). Recruitment, survival and growth of timber-tree seedlings in natural tropical rain forest.
  5. Baur, G. N. (1964). The ecological basis of rainforest management.
  6. Browne, F. G. (1949). Storm forest in Kelantan.
  7. Dangerfield, J. M. (1990). Abundance, biomass and diversity of soil macrofauna in savanna woodland and associated managed habitats.
  8. De Beuzeville, W. A. W. (1946). The climatological basis of forestry. Forestry Commission of New South Wales.
  9. Denslow, J. S. (1987). Tropical rainforest gaps and tree species diversity. Annual review of ecology and systematics, 431-451.
  10. Gleason, H. A., & Cook, M. T. (1926). Plant ecology of Porto Rico, scientific survey of Porto Rico and the Virgin Islands.
  11. Jones, E. W. (1955). Ecological studies on the rain forest of southern Nigeria: IV. The plateau forest of the Okomu Forest Reserve. Journal of Ecology, 43(2), 564-594.
  12. Keay, R. W. J. (1957). Wind-dispersed species in a Nigerian forest. The Journal of Ecology, 471-478.
  13. MacLean, C. D. (1988). Timber resources of Kosrae, Pohnpei, Truk, and Yap, Federated States of Micronesia (Vol. 24). US Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station.
  14. Mudappa, D., & Raman, T. R. S. (2010). Rainforest restoration: A guide to principles and practice. Nature Conservation Foundation.
  15. Park, C. C. (2002). Tropical rainforests. Routledge.
  16. Park, C.C. (1992). Tropical Rainforests (1st ed.). Routledge. https://doi.org/10.4324/9780203413463
  17. Richards, P. W. (1952). The tropical rain forest: an ecological study.
  18. Usher, M. B. (1975). Studies on a wood-feeding termite community in Ghana, West Africa. Biotropica, 217-233.
  19. Wadsworth, F. H., & Englerth, G. H. (1959). Effects of the 1956 hurricane on forests in Puerto Rico. Caribbean Forester, 38-51.
  20. Webb, E. L., Stanfield, B. J., & Jensen, M. L. (1999). Effects of topography on rainforest tree community structure and diversity in American Samoa, and implications for frugivore and nectarivore populations. Journal of Biogeography, 26(4), 887-897.
  21. Webb, L. J. (1958). Cyclones as an ecological factor in tropical lowland rain-forest, North Queensland. Australian Journal of Botany, 6(3), 220-228.

Reference

  1. Aiken, S. R., & Leigh, C. H. (1986). Land use conflicts and rain forest conservation in Malaysia and Australia: The Endau-Rompin and Gordon-Franklin controversies. Land Use Policy, 3(3), 161-179.
  2. Ande, O. T. (1995). Morphogenetic characterization of upland soils in south western Nigeria (Doctoral dissertation, MSc. Thesis, Unpublished. Obafemi Awolowo University, Ile Ife, Nigeria).
  3. Barnard, R. C. (1955). Silviculture in the tropical rain forest of western Nigeria compared with Malayan methods. Empire Forestry Review, 34(4), 355-368.
  4. Barnard, R. C. (1956). Recruitment, survival and growth of timber-tree seedlings in natural tropical rain forest.
  5. Baur, G. N. (1964). The ecological basis of rainforest management.
  6. Browne, F. G. (1949). Storm forest in Kelantan.
  7. Dangerfield, J. M. (1990). Abundance, biomass and diversity of soil macrofauna in savanna woodland and associated managed habitats.
  8. De Beuzeville, W. A. W. (1946). The climatological basis of forestry. Forestry Commission of New South Wales.
  9. Denslow, J. S. (1987). Tropical rainforest gaps and tree species diversity. Annual review of ecology and systematics, 431-451.
  10. Gleason, H. A., & Cook, M. T. (1926). Plant ecology of Porto Rico, scientific survey of Porto Rico and the Virgin Islands.
  11. Jones, E. W. (1955). Ecological studies on the rain forest of southern Nigeria: IV. The plateau forest of the Okomu Forest Reserve. Journal of Ecology, 43(2), 564-594.
  12. Keay, R. W. J. (1957). Wind-dispersed species in a Nigerian forest. The Journal of Ecology, 471-478.
  13. MacLean, C. D. (1988). Timber resources of Kosrae, Pohnpei, Truk, and Yap, Federated States of Micronesia (Vol. 24). US Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station.
  14. Mudappa, D., & Raman, T. R. S. (2010). Rainforest restoration: A guide to principles and practice. Nature Conservation Foundation.
  15. Park, C. C. (2002). Tropical rainforests. Routledge.
  16. Park, C.C. (1992). Tropical Rainforests (1st ed.). Routledge. https://doi.org/10.4324/9780203413463
  17. Richards, P. W. (1952). The tropical rain forest: an ecological study.
  18. Usher, M. B. (1975). Studies on a wood-feeding termite community in Ghana, West Africa. Biotropica, 217-233.
  19. Wadsworth, F. H., & Englerth, G. H. (1959). Effects of the 1956 hurricane on forests in Puerto Rico. Caribbean Forester, 38-51.
  20. Webb, E. L., Stanfield, B. J., & Jensen, M. L. (1999). Effects of topography on rainforest tree community structure and diversity in American Samoa, and implications for frugivore and nectarivore populations. Journal of Biogeography, 26(4), 887-897.
  21. Webb, L. J. (1958). Cyclones as an ecological factor in tropical lowland rain-forest, North Queensland. Australian Journal of Botany, 6(3), 220-228.

Photo
Maulin Parmar
Corresponding author

Department of Botany, Bioinformatics and Climate Change Impacts Management, School of Sciences, Gujarat University, Navrangpura, Ahmedabad – 380009

Photo
Isha pandya
Co-author

Department of Botany, Bioinformatics and Climate Change Impacts Management, School of Sciences, Gujarat University, Navrangpura, Ahmedabad – 380009

Photo
Nainesh Modi
Co-author

Department of Botany, Bioinformatics and Climate Change Impacts Management, School of Sciences, Gujarat University, Navrangpura, Ahmedabad – 380009

Maulin Parmar*, Isha Pandya, Nainesh Modi, Review on Ecology of Rain Forest, Int. J. Sci. R. Tech., 2025, 2 (4), 422-428. https://doi.org/10.5281/zenodo.15248112

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